CA1292391C - Deodorization and cleaning of medium temperature wet off-gases derived from burning of wet waste sludge - Google Patents
Deodorization and cleaning of medium temperature wet off-gases derived from burning of wet waste sludgeInfo
- Publication number
- CA1292391C CA1292391C CA 588236 CA588236A CA1292391C CA 1292391 C CA1292391 C CA 1292391C CA 588236 CA588236 CA 588236 CA 588236 A CA588236 A CA 588236A CA 1292391 C CA1292391 C CA 1292391C
- Authority
- CA
- Canada
- Prior art keywords
- gases
- afterburner
- furnace
- zone
- sludge
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Lifetime
Links
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G7/00—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
- F23G7/06—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
- F23G7/061—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating
- F23G7/065—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating using gaseous or liquid fuel
- F23G7/066—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating using gaseous or liquid fuel preheating the waste gas by the heat of the combustion, e.g. recuperation type incinerator
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/38—Multi-hearth arrangements
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J15/00—Arrangements of devices for treating smoke or fumes
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2900/00—Special features of, or arrangements for incinerators
- F23G2900/00001—Exhaust gas recirculation
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/40—Valorisation of by-products of wastewater, sewage or sludge processing
Landscapes
- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Treating Waste Gases (AREA)
- Treatment Of Sludge (AREA)
- Incineration Of Waste (AREA)
- Gasification And Melting Of Waste (AREA)
Abstract
ABSTRACT OF THE DISCLOSURE
Medium temperature (500°F - 1100°F) wet off-gases from the final drying zone of counterflow incineration of waste sludge are scrubbed and cooled before heating to final high temperature in an after burner and the resulting hot dry gases are used to preheat the scrubbed and cooled gases prior to entry of said gases into the afterburner.
Medium temperature (500°F - 1100°F) wet off-gases from the final drying zone of counterflow incineration of waste sludge are scrubbed and cooled before heating to final high temperature in an after burner and the resulting hot dry gases are used to preheat the scrubbed and cooled gases prior to entry of said gases into the afterburner.
Description
~.~g23~L
DEODORIZATION AND CLEANING OF MEDIUM TEMPERATURE
WET OFF-GASES DERIVED FROM
BURNING OF WET WASTE SLUDGE
Field Of The Invention This invention relates generally to disposal of waste sludge such as the primarily organic municipal sewage sludge and sludges derived from treating industrial wastes. More particularly, the invention is directed to disposing of such sludges by drying and burning in a furnace, such as a multiple hearth furnace, rotary kiln or electric furnace, through which the sludge and hot gases pass counter-currently and there are yielded as separate products dirty, wet off-gases and residual ash.
Backqround A major worldwide problem is the disposal of waste.Typically, wastewater is treated to separate the water, which is reclaimed, from the solids which are disposed of, often by drying and burning.
Waste sludges produced from wastewater treatment are typically dewatered to 16 to 25% total solids with belt presses or centrifuges and 26 - 35% with filter presses. The resulting wet cake is then dried and burned to yield ash and gaseous products which must also be completely oxidized (burned) and cleaned.
The only known effective method of eliminating organic and other combustibles from off-gases is high temperature retention in the presence of adequate oxygen. A retention time of 1 to 3 seconds and a temperature in the range of 1400F - 1800F are normal requirements with the shorter detention time corresponding to higher temperatures.
A major cost factor of prior systems is afterburning of the off-gases containing the products ~
of sludge drying and combustion. These gases, which are wet and loaded with particulates and other contaminants, cannot be used in heat exchangers because they would quickly foul the equipment and create a fire hazard. Because of this, the off-gases are subjected to afterburning as they are twet and dirty) then immediately scrubbed and cooled; and none of the heat content is available to preheat the off-gases.
A related problem inherent in existing systems stems from the need to prepare (heat) the off-gases for immediate afterburning. The economics of afterburning often require that the furnace temperature be so high as to result in undesired "fuming" of heavy metals in the furnace with consequent difficult problems of heavy metal removal.
Summary Of Invention It is the primary object o~ this invention to provide improved ways and means for the disposal of waste sludges by combustion with subsequent cleaning and deodorizing of gaseous products of drying and combustion.
The method o~ the invention requires the step of cooling the medium temperature off-gases from above 500F clear down to an 80F - 120F range and only thereafter reheating the gases to a final temperature of at least 1400F - 2200F.
According to the invention, the initial cooliny and cleaning yields conditioned off-gases that are clean and have been cooled to 80F - 120F are produced. The washing will have removed the particulates while the cooling will have removed by condensation and separation, most moisture and other condensible 3~31 volatile gases. Accordingly, the subsequent afterburner fuel requirements are markedly reduced.
The cooling and cleaning of the off-gases before entry to the afterburner makes it possible to alter furnace operation in a manner to effect even further, but less obvious, afterburner fuel economy. For instance, it is no longer necessary to add as much excess air to the furnace as was previously done. By reducing the air to the furnace, the volume of resulting off-gases is correspondingly reduced this further lowering afterburner fuel requirement.
The features of advantage available through use of the invention include:
1. The furnace can be operated at a higher throughput, as much as 30% higher.
DEODORIZATION AND CLEANING OF MEDIUM TEMPERATURE
WET OFF-GASES DERIVED FROM
BURNING OF WET WASTE SLUDGE
Field Of The Invention This invention relates generally to disposal of waste sludge such as the primarily organic municipal sewage sludge and sludges derived from treating industrial wastes. More particularly, the invention is directed to disposing of such sludges by drying and burning in a furnace, such as a multiple hearth furnace, rotary kiln or electric furnace, through which the sludge and hot gases pass counter-currently and there are yielded as separate products dirty, wet off-gases and residual ash.
Backqround A major worldwide problem is the disposal of waste.Typically, wastewater is treated to separate the water, which is reclaimed, from the solids which are disposed of, often by drying and burning.
Waste sludges produced from wastewater treatment are typically dewatered to 16 to 25% total solids with belt presses or centrifuges and 26 - 35% with filter presses. The resulting wet cake is then dried and burned to yield ash and gaseous products which must also be completely oxidized (burned) and cleaned.
The only known effective method of eliminating organic and other combustibles from off-gases is high temperature retention in the presence of adequate oxygen. A retention time of 1 to 3 seconds and a temperature in the range of 1400F - 1800F are normal requirements with the shorter detention time corresponding to higher temperatures.
A major cost factor of prior systems is afterburning of the off-gases containing the products ~
of sludge drying and combustion. These gases, which are wet and loaded with particulates and other contaminants, cannot be used in heat exchangers because they would quickly foul the equipment and create a fire hazard. Because of this, the off-gases are subjected to afterburning as they are twet and dirty) then immediately scrubbed and cooled; and none of the heat content is available to preheat the off-gases.
A related problem inherent in existing systems stems from the need to prepare (heat) the off-gases for immediate afterburning. The economics of afterburning often require that the furnace temperature be so high as to result in undesired "fuming" of heavy metals in the furnace with consequent difficult problems of heavy metal removal.
Summary Of Invention It is the primary object o~ this invention to provide improved ways and means for the disposal of waste sludges by combustion with subsequent cleaning and deodorizing of gaseous products of drying and combustion.
The method o~ the invention requires the step of cooling the medium temperature off-gases from above 500F clear down to an 80F - 120F range and only thereafter reheating the gases to a final temperature of at least 1400F - 2200F.
According to the invention, the initial cooliny and cleaning yields conditioned off-gases that are clean and have been cooled to 80F - 120F are produced. The washing will have removed the particulates while the cooling will have removed by condensation and separation, most moisture and other condensible 3~31 volatile gases. Accordingly, the subsequent afterburner fuel requirements are markedly reduced.
The cooling and cleaning of the off-gases before entry to the afterburner makes it possible to alter furnace operation in a manner to effect even further, but less obvious, afterburner fuel economy. For instance, it is no longer necessary to add as much excess air to the furnace as was previously done. By reducing the air to the furnace, the volume of resulting off-gases is correspondingly reduced this further lowering afterburner fuel requirement.
The features of advantage available through use of the invention include:
1. The furnace can be operated at a higher throughput, as much as 30% higher.
2. The furnace does not have to be closely controlled to minimize emissions.
3. The furnace can be operated at lower excess air, further increasing capacity and efficiency.
4. The furnace can be operated at a lower temperature to avoid NOX production and the fuming of heavy metals and resulting hard-to-handle contamination of the gases.
- 25 5. The heat content of the furnace cooling air can be better utilized to reduce fuel costs.
6. Fuel consumption for high temperature deodorization can be reduced by 75 - 90%.
7. There is an insignificant fuel cost to go from 1400F to 1800F final combustion temperature.
8. Equipment duty is less severe thereby reducing maintenance and replacement costs.
9. Since the off-gases are thermally oxidized after wet scrubbing, volatiles, such as chloroform, .. . . . . .
~" ~Z~ 3~3~
stripped from the scrubbing water are completely destroyed.
10. The clean stack gases will not result in any visual pollution such as a steam plume.
The furnace is a 25' - 9" OD seven hearth furnace (2,674 ft2) with a design capacity of 22,000 lb~hr of cake at a solids content of 18.6% total solids. ~he furnace was originally designed to operate at up to 1400F afterburning on the bypassed top hearth.
As modified for the invention, the top hearth of the furnace is now used for sludge drying. The new system uses the existing washer-cooler scrubber immediately following the furnace, an added separate afterburner following the scrubber, and an added high efficiency heat exchanger functionally located between the scrubber and afterburner for r~covering heat from the afterburner gases to preheat the conditioneA off-gases from the washer-cooler scrubber ahead of the afterburner.
The majority of heavy metals can be prevented from fuming by keeping them below 1110F (600C). Since the bed of solids and ash in a multiple hearth furnace is 200F - 300F cooler than the gas, combustion of most of the organic vapors can still occur at 1200F -1400F without excessive fuming of heavy metals.
A further improvement in the efficiency and effectiveness of operation according to the invention would be to preheat the afterburner combustion air to 800F - 1200F.
In order that the invention may be more readily understood and carried into effect, reference is made to the accompanying drawings.
2~Z3~
In ?he_ _awings Figure 1 is a diagrammatic view of a system embodying the invention.
Figure 2 is a graph that contrasts the temperature profile of a gas streat produced by practice of this invention with that produced from prior practice.
Figure 3 is a graph depicting typical fuel savings to be achieved by this invention compared to a typical prior system.
Detailed Description Of The Drawinas Figure 1 illustrates the invention embodied in a system that employs a multiple hearth furnace. It comprises a furnace 10 with a plurality of vertically spaced hearths 11. A vertical hollow shaft 12 extends from below the furnace upwardly therethrough. The shaft has a plurality of hollow horizontal arms 13 extending therefrom over the respective hearths and from which depend rakes 14 for stirring solids thereon to cause them to cascade to successively lower hearths.
The vertical shaft and rakes etc. are rotated by a conventional drive 17. Air or other oxygen-bearing gas is introduced into a lower part of the furnace at appropriate points 18 to pass upwardly therethrough as sludge combustion proceeds thence to exit from the top through a suitable conduit 19. Auxiliary fuel and/or air is introduced through a suitable inlet. Wet sludge cake enters through a suitable inlet 15 at the top of the furnace while residual ashes exit through a suitable bottom outlet 20.
Off-gases exiting the drying zone of the top hearth are conducted by the conduit 19 into the cleaner-cooler ~Z3~
system which includes venturi 24 and scrubber 25 whence the scrubber water discharges at 26 while the conditioned off-gases are conducted by means of a conduit 27 and induced draft fan 28 into a heat exchanger 29 where they are preheated by indirect contact with hot, clean gases conducted from the afterburner 31 via a conduit 32 to the heat exchanger 29. The preheated off-gases are conducted to the afterburner 31 by a conduit 33 while the now cooled afterburner discharge gases are released to the atmosphere via a suitable stack 34. Auxiliary fuel and combustion air are inJected into the afterburner at 35.
If furnace cooling air is used as combustion air in the afterburner, it is conveniently conducted from the furnace by conduit 37.
The wet scrubber portion of the system is designed to reduce the gas-entrained particulates to the concentrations required by the various regulatory agencies. This stage will also remove contaminants such as chlorides, sulfates and other fumes or vaporous compounds detrimental to the heat exchanger while condensing moisture from the gases. The conditioned off-gases leaving this stage will be at a temperature in the range from 80F to 120F, will contain very - 25 little moisture (90~ having been removed in scrubber), but will still contain hydrocarbons, organic fumes and complex organic compounds such as dioxins, aldehydes, chloroform, etc., and fixed carbon (soot) requiring removal. Since these conditioned off-gases are free from particulates and essentially dry they are adapted to use in a high efficiency heat exchanger. Thus, in accordance with this invention, they are conducted to a heat exchanger through which the flow in counter-current indirect heat exchange relationship to the hot 3~3~
gases from the afterburner. In this connection, it will be noted that the hot gases from the afterburner are essentially product gases. ~hey are clean and specifically adapted for use in hiyh efficiency heat exchangers for cooling prior to discharge to atmosphere.
The preheated conditioned off-gases leave the heat exchanger at a temperature of 1400F - 1800F. (In fact, as high as 2200F for thermally resistant organics). Depending on the design of the preheater, these gases may be preheated to within 150F of the temperature of the afterburner exhaust gases. Low differential tempQratures are possible in regenerative types of heat exchangers the use of which is enabled by this invention.
The preheated gases are fed into a high temperature (1400F to 1800F) afterburner 31 wherein they are retained for 1 to 3 seconds thereby to reduce the contaminants to an acceptable level for discharge. Hot gases from the afterburner will flow through the preheater to be finally discharges therefrom at a relatively low temperature of 200F to 350F. Because the gases are essentially dry and warm, no visible discharge or plume will result from their release to the atmosphere.
Combustion air to the afterburner can be either ambient or cooling air existing the furnace. The latter is economic since it has been preheated to about 400F to 450F from cooling the furnace center column and rabble arms. If desired, this incoming air can be preheated by heat exchange with afterburner discharge gases.
Since the high efficiency heat-exchanger preheater can be designed to maintain a specific differential ~ ;~9~3~
temperature between afterburner exhaust and incoming preheated off-gases there would be only nominal added fuel usage to heat the afterburner exhaust gases temperature to 1400F, 1500, or even above 1700F.
As shown in the Figure 1 embodiment, the heat exchanger 29 is a single compartment single function unit in which conditioned off-gases enter at one end to flow uninterruptedly therethrough to exit the other end route to the afterburner. Only the conditioned off-gases go through the exchanger in indirect exchange relationship to the counter-flowing afterburner exhaust gases.
Figure 2 illustrates graphically typical savings in auxiliary fuel achievable by modification of an existing prior system to practice the invention.
Figure 3 compares the temperature profile of off-gases from a prior system with the anticipated temperature profile of the off-gases from a the same system practicing the new invention. The upper curve is according to prior practice. It follows the temperature of the off-gases beginning at the final drying hearth of the furnace through the immediate afterburning to high temperature then cooling. The lower curve follows the temperature of off-gases in the new system. The gases start at the same drying hearth, but instead of being heated are immediately cooled and cleaned. Thereafter, they are preheated by heat exchange and finally heated by afterburning to the maximum temperature. It is noteworthy that in the 30 prior practice there are 121,500 lbs/hr of off-gases to be handled in the afterburner whereas in the new practice the load on the afterburner is reduced to 73,250 lbs/hr of gases.
?Z~9~
g Having thus described our invention and the preferred mode of carrying it out, the protection we desire to secure by Letters Patent is def ined in the flowing and the equivalents el[braced therein.
- 25 5. The heat content of the furnace cooling air can be better utilized to reduce fuel costs.
6. Fuel consumption for high temperature deodorization can be reduced by 75 - 90%.
7. There is an insignificant fuel cost to go from 1400F to 1800F final combustion temperature.
8. Equipment duty is less severe thereby reducing maintenance and replacement costs.
9. Since the off-gases are thermally oxidized after wet scrubbing, volatiles, such as chloroform, .. . . . . .
~" ~Z~ 3~3~
stripped from the scrubbing water are completely destroyed.
10. The clean stack gases will not result in any visual pollution such as a steam plume.
The furnace is a 25' - 9" OD seven hearth furnace (2,674 ft2) with a design capacity of 22,000 lb~hr of cake at a solids content of 18.6% total solids. ~he furnace was originally designed to operate at up to 1400F afterburning on the bypassed top hearth.
As modified for the invention, the top hearth of the furnace is now used for sludge drying. The new system uses the existing washer-cooler scrubber immediately following the furnace, an added separate afterburner following the scrubber, and an added high efficiency heat exchanger functionally located between the scrubber and afterburner for r~covering heat from the afterburner gases to preheat the conditioneA off-gases from the washer-cooler scrubber ahead of the afterburner.
The majority of heavy metals can be prevented from fuming by keeping them below 1110F (600C). Since the bed of solids and ash in a multiple hearth furnace is 200F - 300F cooler than the gas, combustion of most of the organic vapors can still occur at 1200F -1400F without excessive fuming of heavy metals.
A further improvement in the efficiency and effectiveness of operation according to the invention would be to preheat the afterburner combustion air to 800F - 1200F.
In order that the invention may be more readily understood and carried into effect, reference is made to the accompanying drawings.
2~Z3~
In ?he_ _awings Figure 1 is a diagrammatic view of a system embodying the invention.
Figure 2 is a graph that contrasts the temperature profile of a gas streat produced by practice of this invention with that produced from prior practice.
Figure 3 is a graph depicting typical fuel savings to be achieved by this invention compared to a typical prior system.
Detailed Description Of The Drawinas Figure 1 illustrates the invention embodied in a system that employs a multiple hearth furnace. It comprises a furnace 10 with a plurality of vertically spaced hearths 11. A vertical hollow shaft 12 extends from below the furnace upwardly therethrough. The shaft has a plurality of hollow horizontal arms 13 extending therefrom over the respective hearths and from which depend rakes 14 for stirring solids thereon to cause them to cascade to successively lower hearths.
The vertical shaft and rakes etc. are rotated by a conventional drive 17. Air or other oxygen-bearing gas is introduced into a lower part of the furnace at appropriate points 18 to pass upwardly therethrough as sludge combustion proceeds thence to exit from the top through a suitable conduit 19. Auxiliary fuel and/or air is introduced through a suitable inlet. Wet sludge cake enters through a suitable inlet 15 at the top of the furnace while residual ashes exit through a suitable bottom outlet 20.
Off-gases exiting the drying zone of the top hearth are conducted by the conduit 19 into the cleaner-cooler ~Z3~
system which includes venturi 24 and scrubber 25 whence the scrubber water discharges at 26 while the conditioned off-gases are conducted by means of a conduit 27 and induced draft fan 28 into a heat exchanger 29 where they are preheated by indirect contact with hot, clean gases conducted from the afterburner 31 via a conduit 32 to the heat exchanger 29. The preheated off-gases are conducted to the afterburner 31 by a conduit 33 while the now cooled afterburner discharge gases are released to the atmosphere via a suitable stack 34. Auxiliary fuel and combustion air are inJected into the afterburner at 35.
If furnace cooling air is used as combustion air in the afterburner, it is conveniently conducted from the furnace by conduit 37.
The wet scrubber portion of the system is designed to reduce the gas-entrained particulates to the concentrations required by the various regulatory agencies. This stage will also remove contaminants such as chlorides, sulfates and other fumes or vaporous compounds detrimental to the heat exchanger while condensing moisture from the gases. The conditioned off-gases leaving this stage will be at a temperature in the range from 80F to 120F, will contain very - 25 little moisture (90~ having been removed in scrubber), but will still contain hydrocarbons, organic fumes and complex organic compounds such as dioxins, aldehydes, chloroform, etc., and fixed carbon (soot) requiring removal. Since these conditioned off-gases are free from particulates and essentially dry they are adapted to use in a high efficiency heat exchanger. Thus, in accordance with this invention, they are conducted to a heat exchanger through which the flow in counter-current indirect heat exchange relationship to the hot 3~3~
gases from the afterburner. In this connection, it will be noted that the hot gases from the afterburner are essentially product gases. ~hey are clean and specifically adapted for use in hiyh efficiency heat exchangers for cooling prior to discharge to atmosphere.
The preheated conditioned off-gases leave the heat exchanger at a temperature of 1400F - 1800F. (In fact, as high as 2200F for thermally resistant organics). Depending on the design of the preheater, these gases may be preheated to within 150F of the temperature of the afterburner exhaust gases. Low differential tempQratures are possible in regenerative types of heat exchangers the use of which is enabled by this invention.
The preheated gases are fed into a high temperature (1400F to 1800F) afterburner 31 wherein they are retained for 1 to 3 seconds thereby to reduce the contaminants to an acceptable level for discharge. Hot gases from the afterburner will flow through the preheater to be finally discharges therefrom at a relatively low temperature of 200F to 350F. Because the gases are essentially dry and warm, no visible discharge or plume will result from their release to the atmosphere.
Combustion air to the afterburner can be either ambient or cooling air existing the furnace. The latter is economic since it has been preheated to about 400F to 450F from cooling the furnace center column and rabble arms. If desired, this incoming air can be preheated by heat exchange with afterburner discharge gases.
Since the high efficiency heat-exchanger preheater can be designed to maintain a specific differential ~ ;~9~3~
temperature between afterburner exhaust and incoming preheated off-gases there would be only nominal added fuel usage to heat the afterburner exhaust gases temperature to 1400F, 1500, or even above 1700F.
As shown in the Figure 1 embodiment, the heat exchanger 29 is a single compartment single function unit in which conditioned off-gases enter at one end to flow uninterruptedly therethrough to exit the other end route to the afterburner. Only the conditioned off-gases go through the exchanger in indirect exchange relationship to the counter-flowing afterburner exhaust gases.
Figure 2 illustrates graphically typical savings in auxiliary fuel achievable by modification of an existing prior system to practice the invention.
Figure 3 compares the temperature profile of off-gases from a prior system with the anticipated temperature profile of the off-gases from a the same system practicing the new invention. The upper curve is according to prior practice. It follows the temperature of the off-gases beginning at the final drying hearth of the furnace through the immediate afterburning to high temperature then cooling. The lower curve follows the temperature of off-gases in the new system. The gases start at the same drying hearth, but instead of being heated are immediately cooled and cleaned. Thereafter, they are preheated by heat exchange and finally heated by afterburning to the maximum temperature. It is noteworthy that in the 30 prior practice there are 121,500 lbs/hr of off-gases to be handled in the afterburner whereas in the new practice the load on the afterburner is reduced to 73,250 lbs/hr of gases.
?Z~9~
g Having thus described our invention and the preferred mode of carrying it out, the protection we desire to secure by Letters Patent is def ined in the flowing and the equivalents el[braced therein.
Claims (10)
1. The method for waste sludge incineration comprising the steps of moving sludge through a thermal treatment zone counter-currently to the flow of combustion gases and products therethrough while maintaining conditions in the treatment zone sequentially to dry then combust said sludge thereby to yield and discharge as separate products solid residue and off-gases which off-gases contain particulates as well as vapors of water and other materials and are at a temperature in the range from about 500°F to about 1100°F; washing and cooling said off-gases to yield conditioned off-gases that are substantially free from particulates and are at a temperature in the range from about 80°F to about 120°F; introducing said conditioned off-gases into an afterburner zone, burning fuel in combustion air in said afterburner zone; retaining said conditioned off-gases in said afterburner zone to produce hot fully treated off-gases that are at a temperature of from 1400°F to about 2200°F; flowing said hot fully treated off-gases and said conditioned off-gases through a heat exchange zone before said conditioned off-gases are heated in said afterburner zone thereby to preheat said conditioned off-gases while cooling said fully treated gases; and discharging said fully treated gases.
2. The method according to claim 1 in which combustion supporting gases in said treatment zone initially contain free oxygen in an amount not exceeding seventy five percent of that amount stoichiometrically required to oxidize all of the carbon, hydrogen, oxygen, nitrogen and sulfur in the sludge and fuel supplied to said zone to yield carbon dioxide, water and sulfur dioxide.
3. The method according to claim 1 in which the combustion supporting gases and off-gases supplied to said afterburner contain free oxygen in an amount in the range from about thirty percent to about seventy five percent of that stoichiometrically required to oxidize all fuel and oxidizable constituents in said off-gases supplied to said afterburner.
4. The method according to claim 1 in which the combustion air supplied to the afterburner zone is first preheated by indirect heat exchange contact with the hot fully treated off-gases from the afterburner zone.
5. The method according to claim 1 in which atmospheric air is used as cooling air to cool said solids treatment zone and thereby to preliminarily heat said cooling air, and said cooling air is thereafter further preheated by heat exchange with said hot fully treated gases from the afterburner then is supplied to said afterburner to act as combustion air therein.
6. The method according to any of claims 4 or 5 in which hot fully treated off-gases flow in heat exchange relationship first to said combustion air then to said conditioned off-gases.
7. The method according to claim 1 in which treatment zone conditions are controlled to maintain the sludge solids and ash therein at a temperature below that at which substantial quantities of heavy metals contained in said sludge and ash are fumed.
8. Apparatus for disposal of wet waste sludge and resulting off-gases, comprising in combination of furnace of the type adapted to dry and burn sludge as it passes therethrough counter to the flow of gases, including combustion products, therethrough, said furnace being adapted to dry sludge in a zone whence off-gases discharge from said furnace; a cleaner and scrubber adapted to wash and cool off-gases to the temperature range of from about 80°F to about 120°F, a heat exchanger of the type in which heat exchange occurs between gases, an afterburner that includes a combustion chamber adapted to burn fuel and gases in the presence of oxygen to yield hot gases in the range from about 1400°F to about 1700°F, a first conduit located to conduct off-gases from said furnace to said cleaner and scrubber, a second conduit located to conduct gases discharged from said scrubber to said heat-exchanger, a third conduit located to conduct off-gases from said heat exchanger to said afterburner, a fourth conduit located to conduct hot gases from said afterburner to said heat exchanger, and a final outlet on said heat exchanger for discharging said last named gases therefrom after passage therethrough.
9. The apparatus as claimed in claim 8 wherein said apparatus is arranged in series in order stated;
a counter-flow furnace having a separate outlet for solid residue and off-gases, an off-gas scrubber and cooler, a heat exchanger, an afterburner, gas flow guidance means functionally connecting said compartments so that off-gases from said furnace flow are guided to flow without interruption sequentially through said components, conduit means for conducting gases from said afterburner to said heat exchanger, and final outlet means including a stack to release afterburner gases from said heat exchanger.
a counter-flow furnace having a separate outlet for solid residue and off-gases, an off-gas scrubber and cooler, a heat exchanger, an afterburner, gas flow guidance means functionally connecting said compartments so that off-gases from said furnace flow are guided to flow without interruption sequentially through said components, conduit means for conducting gases from said afterburner to said heat exchanger, and final outlet means including a stack to release afterburner gases from said heat exchanger.
10. Apparatus according to claim 9 with the addition to said furnace of a furnace cooling air inlet and furnace cooling air outlet, and independent conduit means for conducting said cooling air from said furnace to said afterburner.
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US219,721 | 1988-07-15 | ||
| US07/219,721 US4901654A (en) | 1988-07-15 | 1988-07-15 | Deodorization and cleaning of medium temperature wet off-gases derived from burning of wet waste sludge |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CA1292391C true CA1292391C (en) | 1991-11-26 |
Family
ID=22820508
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CA 588236 Expired - Lifetime CA1292391C (en) | 1988-07-15 | 1989-01-13 | Deodorization and cleaning of medium temperature wet off-gases derived from burning of wet waste sludge |
Country Status (8)
| Country | Link |
|---|---|
| US (1) | US4901654A (en) |
| JP (1) | JPH0226614A (en) |
| AU (1) | AU618825B2 (en) |
| CA (1) | CA1292391C (en) |
| DE (1) | DE3902611C2 (en) |
| FR (1) | FR2634192B1 (en) |
| GB (1) | GB2233435B (en) |
| WO (1) | WO1990000701A1 (en) |
Families Citing this family (18)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4440650A (en) * | 1981-11-02 | 1984-04-03 | Cosden Technology, Inc. | Process for enhancing recovery of oil from oil-bearing earth formations |
| US4917027A (en) * | 1988-07-15 | 1990-04-17 | Albertson Orris E | Sludge incineration in single stage combustor with gas scrubbing followed by afterburning and heat recovery |
| US5319176A (en) * | 1991-01-24 | 1994-06-07 | Ritchie G. Studer | Plasma arc decomposition of hazardous wastes into vitrified solids and non-hazardous gasses |
| US5222446A (en) * | 1991-05-29 | 1993-06-29 | Edwards A Glen | Non-polluting incinerator |
| US5309849A (en) * | 1992-05-22 | 1994-05-10 | Andritz Tcw Engineering Gmbh | Sludge drying system with recycling exhaust air |
| US5318184A (en) * | 1992-09-10 | 1994-06-07 | Georg Krebs | Sludge drying system |
| GB9220428D0 (en) * | 1992-09-28 | 1992-11-11 | Barr Derek J | Sludge treating process and apparatus |
| GB9308537D0 (en) * | 1993-04-24 | 1993-06-09 | Bradshaw Handley Consultants L | Method and apparatus for consuming volatiles or solids entrained in a process plant fluid |
| DE4344700C2 (en) * | 1993-12-27 | 1999-01-28 | Eisenmann Kg Maschbau | Device for cleaning polluted exhaust air from industrial plants by regenerative post-combustion |
| US5957064A (en) * | 1997-11-28 | 1999-09-28 | Barry; Louis T. | Method and apparatus for operating a multiple hearth furnace |
| US7669349B1 (en) * | 2004-03-04 | 2010-03-02 | TD*X Associates LP | Method separating volatile components from feed material |
| CN100458284C (en) * | 2005-12-15 | 2009-02-04 | 沈福昌 | A complete set of equipment for incinerating waste |
| JP2008194688A (en) * | 2008-02-13 | 2008-08-28 | Taiheiyo Cement Corp | Dioxin-pyrolyzing method |
| US8568569B2 (en) * | 2009-12-09 | 2013-10-29 | Chavond-Barry Engineering | Method and apparatus for efficient production of activated carbon |
| US20110197797A1 (en) * | 2010-02-18 | 2011-08-18 | Chavond-Barry Engineering Corp. | Method and apparatus for efficient production of activated carbon |
| CN103528076A (en) * | 2013-10-21 | 2014-01-22 | 昆山市盛兴设备安装有限公司 | Exhaust gas incineration disposal system |
| CN109373315A (en) * | 2018-11-21 | 2019-02-22 | 贵州智慧能源科技有限公司 | A kind of venturi burner being capable of handling complex component sewage |
| CN116576473A (en) * | 2023-06-09 | 2023-08-11 | 南方电网调峰调频发电有限公司储能科研院 | Exhaust treatment device in thermal runaway process of lithium battery |
Family Cites Families (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US2655883A (en) * | 1949-01-19 | 1953-10-20 | Warren S Martin | Apparatus for heat treatment of sewage sludge and method adapted to be carried out therein |
| US2744477A (en) * | 1951-12-08 | 1956-05-08 | Pacific Foundry Company Ltd | Incinerator |
| JPS48101357A (en) * | 1972-04-03 | 1973-12-20 | ||
| US4050389A (en) * | 1976-07-19 | 1977-09-27 | Nichols Engineering & Research Corporation | Method and apparatus for incinerating waste material |
| US4215637A (en) * | 1979-04-02 | 1980-08-05 | Envirotech Corporation | System for combustion of wet waste materials |
| US4311103A (en) * | 1979-05-16 | 1982-01-19 | Yasuo Hirose | Incineration system for sewage sludge |
-
1988
- 1988-07-15 US US07/219,721 patent/US4901654A/en not_active Expired - Lifetime
-
1989
- 1989-01-09 JP JP1002666A patent/JPH0226614A/en active Pending
- 1989-01-13 CA CA 588236 patent/CA1292391C/en not_active Expired - Lifetime
- 1989-01-28 DE DE19893902611 patent/DE3902611C2/en not_active Expired - Fee Related
- 1989-06-28 WO PCT/US1989/002794 patent/WO1990000701A1/en not_active Ceased
- 1989-06-28 AU AU38495/89A patent/AU618825B2/en not_active Ceased
- 1989-07-12 FR FR8909432A patent/FR2634192B1/en not_active Expired - Fee Related
-
1990
- 1990-03-14 GB GB9005971A patent/GB2233435B/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| AU618825B2 (en) | 1992-01-09 |
| FR2634192A1 (en) | 1990-01-19 |
| GB9005971D0 (en) | 1990-08-01 |
| US4901654A (en) | 1990-02-20 |
| GB2233435A (en) | 1991-01-09 |
| DE3902611A1 (en) | 1990-01-18 |
| DE3902611C2 (en) | 1997-04-30 |
| JPH0226614A (en) | 1990-01-29 |
| GB2233435B (en) | 1992-10-21 |
| WO1990000701A1 (en) | 1990-01-25 |
| AU3849589A (en) | 1990-02-05 |
| FR2634192B1 (en) | 1993-08-13 |
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Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| MKLA | Lapsed |